JPH07180828A - Heat-generation process and plant simultaneously functioningas regeneration of adsorbent and fertilizer production - Google Patents
Heat-generation process and plant simultaneously functioningas regeneration of adsorbent and fertilizer productionInfo
- Publication number
- JPH07180828A JPH07180828A JP6286055A JP28605594A JPH07180828A JP H07180828 A JPH07180828 A JP H07180828A JP 6286055 A JP6286055 A JP 6286055A JP 28605594 A JP28605594 A JP 28605594A JP H07180828 A JPH07180828 A JP H07180828A
- Authority
- JP
- Japan
- Prior art keywords
- adsorbent
- solution
- regeneration
- regenerated
- heat
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Pending
Links
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/46—Removing components of defined structure
- B01D53/48—Sulfur compounds
- B01D53/50—Sulfur oxides
- B01D53/501—Sulfur oxides by treating the gases with a solution or a suspension of an alkali or earth-alkali or ammonium compound
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01C—AMMONIA; CYANOGEN; COMPOUNDS THEREOF
- C01C1/00—Ammonia; Compounds thereof
- C01C1/24—Sulfates of ammonium
- C01C1/244—Preparation by double decomposition of ammonium salts with sulfates
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/14—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by absorption
- B01D53/1456—Removing acid components
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/46—Removing components of defined structure
- B01D53/48—Sulfur compounds
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/46—Removing components of defined structure
- B01D53/48—Sulfur compounds
- B01D53/50—Sulfur oxides
- B01D53/508—Sulfur oxides by treating the gases with solids
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/46—Removing components of defined structure
- B01D53/54—Nitrogen compounds
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05C—NITROGENOUS FERTILISERS
- C05C3/00—Fertilisers containing other salts of ammonia or ammonia itself, e.g. gas liquor
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/30—Fuel from waste, e.g. synthetic alcohol or diesel
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P20/00—Technologies relating to chemical industry
- Y02P20/141—Feedstock
Landscapes
- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Organic Chemistry (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Analytical Chemistry (AREA)
- General Chemical & Material Sciences (AREA)
- Environmental & Geological Engineering (AREA)
- Health & Medical Sciences (AREA)
- Biomedical Technology (AREA)
- Inorganic Chemistry (AREA)
- Treating Waste Gases (AREA)
- Fertilizers (AREA)
- Chimneys And Flues (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
Abstract
Description
【0001】[0001]
【発明の背景】本発明は燃焼フュームの処理手段を含む
発熱器の分野に関する。硫黄や窒素を多量に含む燃料を
用いる発熱器では、燃焼によって硫黄酸化物や窒素酸化
物、それに可燃化合物の燃え残りが多量に排出されるた
め汚染問題が生じる。BACKGROUND OF THE INVENTION The present invention relates to the field of heat generators including means for treating combustion fumes. In a heat generator using a fuel containing a large amount of sulfur or nitrogen, a large amount of sulfur oxides, nitrogen oxides, and unburned combustible compounds are discharged by combustion, which causes a pollution problem.
【0002】このような排ガスに対する規制がますます
厳しくなり、硫黄含量の高い燃料はほとんど使用できな
くなっている。Regulations on such exhaust gas are becoming more and more stringent, and fuels having a high sulfur content are almost unusable.
【0003】この問題を解決するために種々の技術が提
案されている。Various techniques have been proposed to solve this problem.
【0004】フランス特許FR-2,609,150によると、硫黄
含量の高い燃料を使用できる発熱器が排出する硫黄酸化
物、特に亜硫酸ガスの発生を少なくすることができる。
そのために、3つの主要な部材を組合せて小型アセンブ
リを形成する。すなわち好ましくは冷壁燃焼室、燃焼ガ
スの顕熱を回収する廃熱回収ボイラー、有意な内部交換
面を持たず上流の炉と下流の交換器の間を通過するガス
の脱硫を目的とする中間循環床である。According to French patent FR-2,609,150, it is possible to reduce the production of sulfur oxides, in particular sulfurous acid gas, emitted by heating elements which can use fuels with a high sulfur content.
To that end, the three main components are combined to form a miniature assembly. That is, preferably a cold wall combustion chamber, a waste heat recovery boiler for recovering sensible heat of combustion gas, an intermediate for desulfurization of gas passing between an upstream furnace and a downstream exchanger without a significant internal exchange surface. It is a circulating bed.
【0005】このプラントの脱硫効果を改良したものが
フランス特許FR-2,636,720に提案されている。An improved desulfurization effect of this plant is proposed in French Patent FR-2,636,720.
【0006】後者のタイプの発熱器では、硫黄酸化物を
捕捉するために石灰質の粉状吸着剤が懸濁液あるいは乾
燥粉末の形で注入される。この工程は約1000℃で行
われる。In the latter type of heater, a calcareous pulverulent adsorbent is injected in the form of a suspension or a dry powder in order to trap sulfur oxides. This step is performed at about 1000 ° C.
【0007】かかるボイラーにおける大きな問題は、多
量の使用済み吸着剤、主に生石灰と無水硫酸カルシウム
の生成に関するものであり、その処分はますます困難と
なり、費用がかかりかつ一般大衆の評判が悪い。A major problem in such boilers relates to the production of large quantities of spent adsorbents, primarily quicklime and anhydrous calcium sulfate, which are becoming increasingly difficult, expensive, and unpopular with the public.
【0008】この問題を解決するための既知の方法とし
て、フランス特許FR-2,671,855に開示されているよう
に、再生可能な苦灰質系吸着剤と呼ばれる吸着剤を使用
するものがあり、これは最終的な固体物質の排出を非常
に少なくし、その一方で非常に適正にフュームを処理す
ることができる。A known method to solve this problem is to use an adsorbent called regenerable dolomitic adsorbent, as disclosed in French patent FR-2,671,855, which is the final The emission of solid solid substances is very low, while the fumes can be treated very well.
【0009】この従来技術によれば、使用済み吸着剤を
再生することによって硫黄が濃縮SO2とH2Sの形で放
出される。これらの化学物質を貯留ホッパーに回収し、
その後例えば硫黄を元素の形に転換するためにクラウス
プラントに装填する。しかし、これらの「後処理」は費
用がかかることが分かり、かかる技術を必要とするユー
ザーが積極的に使おうと思うものではなかった。According to this prior art, the sulfur is released in the form of concentrated SO2 and H2S by regenerating the spent adsorbent. Collect these chemicals in the storage hopper,
Then, for example, the Claus plant is loaded in order to convert sulfur into its elemental form. However, these "post-treatments" proved to be expensive and were not something that users in need of such technology would be willing to use.
【0010】[0010]
【発明の要旨】本発明は、発熱器の燃焼フュームを処理
する新しい方法を提案する。使用した吸着剤を再生する
ため、最終排出物の量を減らすことができ、吸着剤の使
用も少なくてすむ。SUMMARY OF THE INVENTION The present invention proposes a new method of treating the combustion fumes of a heating element. Since the used adsorbent is regenerated, the amount of final emission can be reduced and the amount of adsorbent used can be reduced.
【0011】しかも、使用する吸着剤が苦灰質系のもの
ではなく石灰質系であり、石灰あるいは天然の石灰岩は
それ自体安価なので、本発明の実施にあまり費用がかか
らない。Moreover, since the adsorbent used is not a bitter ash type but a calcareous type, and lime or natural limestone itself is inexpensive, the present invention is not so expensive to implement.
【0012】さらに、本発明によりフューム中に捕捉さ
れる硫黄の品質が向上し、肥料の品質もよくなる。とい
うのは、再生過程で得られる硫黄含有物質それ自体が肥
料であり、また肥料によってはその組成として加えても
よい。Furthermore, the present invention improves the quality of the sulfur trapped in the fumes and improves the quality of the fertilizer. This is because the sulfur-containing substance obtained in the regeneration process itself is a fertilizer, and depending on the fertilizer, it may be added as its composition.
【0013】本発明に付随するこの高品質化が、本発明
の使用を有利なものにしている。This improvement in quality associated with the present invention makes it advantageous for its use.
【0014】しかも、本出願の目的であるこの新しい技
術は、「固体廃棄物をゼロにする」という概念に近いも
のである。つまりその概念とは、容易に理解できるよう
に、燃焼生成物を安価に利用するためにかかる生成物の
品質を向上させようというものである。Moreover, this new technique, which is the object of the present application, is close to the concept of "zero solid waste". So the concept is, as it is easy to understand, to improve the quality of combustion products in order to use them cheaply.
【0015】上記目的は、本発明によって達成できる。
本発明の目的は、特に脱硫ゾーンを有する発熱器と、除
塵手段と、除塵手段から出る排ガスを排出するための煙
突と、使用済み吸着剤の再生手段と、再生吸着剤の濾過
手段とを含む発熱プラントである。The above object can be achieved by the present invention.
The object of the present invention comprises in particular a heating element having a desulfurization zone, a dust removal means, a chimney for discharging the exhaust gas emitted from the dust removal means, a regeneration means for the spent adsorbent, and a filtration means for the regenerated adsorbent. It is a heat generation plant.
【0016】本発明によれば、使用する吸着剤は石灰質
であり、プラントはさらに再生に使用する溶液を調製す
る手段を含んでもよく、濾過手段から出る硫黄含有物を
肥料にしてもよい。According to the invention, the adsorbent used is calcareous, the plant may further comprise means for preparing the solution used for regeneration, and the sulfur-containing material leaving the filtration means may be fertilizer.
【0017】さらに正確には、溶液調製手段は交換器で
構成してもよく、貯留手段から供給されるアンモニア溶
液を除塵手段から排出されるガスの一部と接触させ、そ
の溶液に貯留手段に蓄えられた二酸化炭素を加える。調
製された溶液は濃縮炭酸アンモニウム溶液である。More precisely, the solution preparation means may be constituted by an exchanger, and the ammonia solution supplied from the storage means is brought into contact with a part of the gas discharged from the dust removal means, and the solution is stored in the storage means. Add the stored carbon dioxide. The solution prepared is a concentrated ammonium carbonate solution.
【0018】熱交換器を接触器とともに作動させてもよ
い。The heat exchanger may be operated with the contactor.
【0019】発熱器には、好ましくは燃焼室、脱硫およ
び/または脱窒室、対流交換器が設けられ、脱硫室には
再生吸着剤、非再生吸着剤および水酸化アンモニウムの
供給ラインを設ける。The heating device is preferably provided with a combustion chamber, a desulfurization and / or denitrification chamber and a convection exchanger, and the desulfurization chamber is provided with supply lines for regenerated adsorbent, non-regenerated adsorbent and ammonium hydroxide.
【0020】さらに、吸着剤再生手段は濃縮炭酸アンモ
ニウム溶液と塵埃分離器からでる使用済み石灰質吸着剤
の一部が送られる少なくとも1基の反応器で構成しても
よい。該反応器には混合液を攪拌する手段とできれば熱
回収手段を設ける。Further, the adsorbent regeneration means may be composed of a concentrated ammonium carbonate solution and at least one reactor to which a part of the spent calcareous adsorbent discharged from the dust separator is sent. The reactor is provided with a means for stirring the mixed solution and preferably a heat recovery means.
【0021】また、本発明は特に以下の工程からなるプ
ロセスに関する。 − 発熱器で燃焼を行う − 該発熱器内の燃焼からの排出ガスを脱硫、脱窒する − 処理済み排出ガスの熱交換を行う − 処理済み排出ガスの除塵を行う − 吸着剤を回収し、その一部を脱硫/脱窒ゾーンに向
けて再循環させ、残りを再生ゾーンに供給する − 除塵したフュームを大気中に放出する − 吸着剤を再生する − 再生吸着剤を脱硫/脱窒ゾーンに再循環させる − 再生段階で出たフュームを排出するThe present invention also particularly relates to a process comprising the following steps. -Combustion in the heat generator-Desulfurization and denitrification of the exhaust gas from the combustion in the heat generator-Heat exchange of the treated exhaust gas-Dust removal of the treated exhaust gas-Recovering the adsorbent, Part of it is recirculated to the desulfurization / denitrification zone, and the rest is supplied to the regeneration zone.-Fume from which dust is removed is released into the atmosphere.-Adsorbent is regenerated. Recirculate-Discharge fumes from the regeneration stage
【0022】本発明によれば、発熱プロセスはさらに以
下からなる。 − 石灰質吸着剤を使用する − (i)再生工程の前に水酸化アンモニウムと二酸化炭
素で炭酸アンモニウム溶液 を調製する − 再生工程中、少なくとも1基の反応器において該溶
液と再生しようとする石灰質吸着剤とを混合する − 該再生によって得た混合液を濾過する − 再生済み石灰質吸着剤を脱硫/脱窒ゾーンに再循環
させる前に該吸着剤を回収する一方、硫酸アンモニウム
溶液も回収するAccording to the invention, the exothermic process further comprises: -Use a calcareous adsorbent- (i) Prepare an ammonium carbonate solution with ammonium hydroxide and carbon dioxide before the regeneration step-Calcium adsorption to be regenerated with the solution in at least one reactor during the regeneration step Mixing with the agent-filtering the mixture obtained by the regeneration-recovering the regenerated calcareous adsorbent before recycling it to the desulfurization / denitrification zone, while also recovering the ammonium sulphate solution
【0023】(i)で用いる二酸化炭素は発熱器からでる
フュームからおよび/または特定の容器から得られる利
点がある。The carbon dioxide used in (i) has the advantage that it can be obtained from the fumes leaving the heating element and / or from a specific container.
【0024】他の特長として、このプロセスを炭酸アン
モニウム溶液の調製および/または吸着剤再生と同時に
熱交換を行う構成にしてもよい。As another feature, the process may be configured to perform heat exchange simultaneously with the preparation of the ammonium carbonate solution and / or regeneration of the adsorbent.
【0025】好ましくは、再生を数基の反応器を用いて
連続して行う。The regeneration is preferably carried out continuously using several reactors.
【0026】炭酸カルシウムおよび/または二酸化炭素
を種々の反応器に追加供給してもよい。Calcium carbonate and / or carbon dioxide may additionally be fed to the various reactors.
【0027】最終の濾過工程は水を勢いよく逆流させて
行ってもよい。The final filtration step may be carried out with a vigorous backflow of water.
【0028】再生吸着剤を回収した後、再循環させる前
にさらに処理することもできる。After recovery of the regenerated adsorbent, it may be further processed before recycling.
【0029】再生吸着剤を乾燥した形で使用する場合
は、追加処理として乾燥を行う。When the regenerated adsorbent is used in a dried form, it is dried as an additional treatment.
【0030】懸濁液の形で使用する場合は、追加処理と
して水分を調整するおよび/またはさらに安定剤を加え
る工程を行う。When used in the form of a suspension, a step of adjusting the water content and / or adding a stabilizer is additionally performed.
【0031】本発明のその他の特長、利点は、以下に非
制限的に挙げる実施例の説明および添付の図面から明ら
かであろう。Other features and advantages of the present invention will be apparent from the following non-limiting description of embodiments and the accompanying drawings.
【0032】[0032]
【好ましい実施例の説明】このプラントの基本的な要素
のうちいくつかについては本技術分野の熟練者には既知
の事柄なので、ここでは詳細に述べない。それらの特定
の目的および/または他の要素との関連がある場合のみ
以下の記載に含める。DESCRIPTION OF THE PREFERRED EMBODIMENTS Some of the basic elements of this plant are known to those skilled in the art and will not be described in detail here. Included in the following description only in connection with their specific purpose and / or other elements.
【0033】図に示すプラントには発熱器1が含まれ、
発熱器は3つの要素に分かれる。すなわち、ガスの流れ
る方向に、加熱装置(図示せず)を有する燃焼室1-
a、中間の脱硫脱窒室1-bおよび対流熱交換ゾーン1-
cである。脱硫脱窒室1-bには、ライン2を通って貯
留容器4から水酸化アンモニウムが、ライン3-aを通
って再循環された非再生吸着剤が、そしてライン3-b
を通って再生吸着剤が供給される。燃焼排出ガスはライ
ン5を通って発熱器1から排出され、除塵装置6に流れ
る。次いで吸着剤を含まないフュームが移送ライン8を
経由して煙突7に送られる。The plant shown in the figure includes a heat generator 1.
The heating element is divided into three elements. That is, the combustion chamber 1-having a heating device (not shown) in the gas flow direction
a, intermediate desulfurization and denitrification chamber 1-b and convection heat exchange zone 1-
c. In the desulfurization and denitrification chamber 1-b, ammonium hydroxide from the storage container 4 is passed through the line 2, the non-regenerated adsorbent recirculated through the line 3-a, and the line 3-b.
The regenerated adsorbent is supplied through. The combustion exhaust gas is discharged from the heat generator 1 through the line 5 and flows to the dust removing device 6. The fumes without adsorbent are then sent to the chimney 7 via the transfer line 8.
【0034】本発明のプラントはさらに、例えば充填カ
ラムのような気液接触器9を含む。この接触器9には、
その上部にライン10を通って貯留容器4からアンモニ
ア溶液が供給され、下部にはライン11を通ってCO2
含有ガスが供給される。ライン11には、主フューム管
8に引き込んだものが分岐回路12を介して供給され、
またCO2発生器またはCO2貯留容器14に接続したラ
イン13からも供給されるのが好ましい。The plant of the present invention further comprises a gas-liquid contactor 9, such as a packed column. In this contactor 9,
Ammonia solution is supplied from the storage container 4 to the upper part thereof through the line 10 and CO2 is supplied to the lower part thereof through the line 11.
A containing gas is supplied. What is drawn into the main fume pipe 8 is supplied to the line 11 through the branch circuit 12,
It is also preferably supplied from a line 13 connected to a CO2 generator or a CO2 storage container 14.
【0035】アンモニア溶液は接触器9を通って濾過さ
れ、進むに従い炭酸アンモニウム濃度が高くなる。濃縮
炭酸アンモニウム溶液はライン15を通って接触器9の
底部で抽出される。The ammonia solution is filtered through the contactor 9, and the ammonium carbonate concentration increases as it proceeds. The concentrated ammonium carbonate solution is extracted through line 15 at the bottom of contactor 9.
【0036】接触器9はいくつかの部分9-a、9-b・・
・に分かれており、それらの間で溶液が抽出され熱交換
器16によって冷却される。The contactor 9 comprises several parts 9-a, 9-b ...
Divided into, between which the solution is extracted and cooled by the heat exchanger 16.
【0037】吸着剤の再生は、連続して配列した反応器
17-a、17-b・・・で行う。これらの反応器には攪拌
混合手段18を設ける。反応器のうちいくつかに、特に
最初の装置に、液相に浸漬したチューブの束からなる熱
抽出手段19を設けるのが好ましい。Regeneration of the adsorbent is carried out in the reactors 17-a, 17-b ... Which are arranged in series. A stirring and mixing means 18 is provided in these reactors. It is preferred to provide some of the reactors, especially the first device, with a heat extraction means 19 consisting of a bundle of tubes immersed in the liquid phase.
【0038】使用済み吸着剤はライン20を通って該反
応器17-a(原文のママ)の少なくとも1基に供給さ
れ、炭酸アンモニウム溶液がライン21-aを通って第
1の反応器17-aに供給される。Spent adsorbent is fed through line 20 to at least one of the reactors 17-a (texture) and ammonium carbonate solution is passed through line 21-a to the first reactor 17-a. is supplied to a.
【0039】無水物から硫酸アンモニウムへの転換を促
進させるために、次の反応器17-bなどへの炭酸アン
モニウムの供給をライン21−bなどを介して行う。硫
酸アンモニウムと残留炭酸カルシウムを含む溶液はライ
ン23を通ってフィルター22に送られる。In order to accelerate the conversion of the anhydride to ammonium sulfate, the ammonium carbonate is supplied to the next reactor 17-b or the like through a line 21-b or the like. The solution containing ammonium sulphate and residual calcium carbonate is sent through line 23 to filter 22.
【0040】炭酸カルシウム粒子をほとんど含まない硫
酸アンモニウム溶液はライン24を通ってフィルター2
2から流出する。この液をさらに分解器(図示せず)に
送って炭酸カルシウム残量をさらに減らし、最終製品の
望ましい粒径に合わせた蒸発器/造粒器(図示せず)に
装入してもよい。The ammonium sulfate solution containing almost no calcium carbonate particles is passed through the line 24 to the filter 2
It flows out from 2. This liquor may be further sent to a decomposer (not shown) to further reduce the calcium carbonate balance and charged to an evaporator / granulator (not shown) tailored to the desired particle size of the final product.
【0041】炭酸カルシウムはフィルター22からライ
ン25に泥状で送られるが、その水分はライン26を介
して水を供給することにより調整する。この最終的な水
分供給により、貯留、流量制御ができ、ライン3-bに
よる輸送、再生吸着剤の脱硫・脱窒室1-bへの再注入
も最適の条件のもとに行うことができる。The calcium carbonate is sent from the filter 22 to the line 25 in the form of mud, and the water content is adjusted by supplying water via the line 26. By this final water supply, storage and flow rate control are possible, and transportation by line 3-b and reinjection of regenerated adsorbent into desulfurization / denitrification chamber 1-b can also be performed under optimal conditions. .
【0042】本出願の目的をさらに理解するために、上
記のプラントでの好ましい実施手順を以下に説明する。In order to further understand the purpose of the present application, the preferred procedure of implementation in the above plant is described below.
【0043】概略すると、本発明プロセスは発熱器1内
でのフュームの脱硫および脱窒工程からなり、該工程は
チューブレスゾーン1−bあるいはその目的のために設
けた別の内部ゾーンで行うのが好ましい。再生吸着剤は
特に硫黄酸化物を回収するのに使われ、高濃度の水酸化
アンモニウム溶液は燃焼フューム中に噴霧して窒素酸化
物を減少させる。これによりフュームを脱窒するための
水酸化アンモニウムの貯留施設がすでにその場に備わっ
ているという利点がある。In summary, the process of the present invention comprises a step of desulfurizing and denitrifying fumes in the heat generator 1, which step is carried out in the tubeless zone 1-b or another internal zone provided for that purpose. preferable. Regenerated adsorbents are especially used to recover sulfur oxides, and concentrated ammonium hydroxide solutions are sprayed into the combustion fumes to reduce nitrogen oxides. This has the advantage that an ammonium hydroxide storage facility for denitrifying fumes is already in place.
【0044】最終の除塵工程が発熱器1の出口でも行わ
れ、ここでほとんどの吸着剤が回収される。この除塵
は、本技術分野の熟練者には公知の静電集塵器などの手
段6によって行う。The final dust removal process is also performed at the outlet of the heat generator 1, where most of the adsorbent is recovered. This dust removal is performed by means 6 such as an electrostatic precipitator known to those skilled in the art.
【0045】塵埃分離器6の出口で使用済み吸着剤の一
部は特に処理せずにライン3-aを介して直接発熱器1
に再循環される。フュームの脱硫効率や吸着剤の使用率
(つまり吸着剤の硫酸化率)を高めるためである。残り
の使用済み吸着剤はライン20を介して再生ユニット1
7に送られる。At the outlet of the dust separator 6, a part of the used adsorbent is not particularly treated, and the heat generator 1 is directly fed through the line 3-a.
Be recycled. This is to increase the desulfurization efficiency of the fumes and the adsorbent usage rate (that is, the adsorbent sulfation rate). The remaining used adsorbent is recycled to the regeneration unit 1 via line 20.
Sent to 7.
【0046】再生プロセスの第1段階は以下の反応機序
に従って炭酸アンモニウム溶液を調製することからな
る。 2NH4OH+CO2(NH4)2CO3+H2OThe first step of the regeneration process consists of preparing an ammonium carbonate solution according to the following reaction mechanism. 2NH4OH + CO2 (NH4) 2CO3 + H2O
【0047】この調製には、フュームを脱窒するための
水酸化アンモニウムを用いてもよく、あるいはその他の
アンモニアあるいは水酸化アンモニウムを用いてもよ
い。二酸化炭素の供給源としては、再生装置(原文のマ
マ)から排出されるフュームでもよい。ライン12によ
って塵埃分離器6の出口でかかる引き抜きを行うことが
できる。これらのフュームは、例えば膜などの既知のガ
ス分離手段14や高CO2ガス発生器などによってCO2
含量を高めてもよい。Ammonium hydroxide for denitrifying fumes may be used in this preparation, or other ammonia or ammonium hydroxide may be used. The carbon dioxide supply source may be fumes discharged from the regeneration device (original mama). The line 12 allows such an extraction to take place at the outlet of the dust separator 6. These fumes are converted to CO2 by a known gas separation means 14 such as a membrane or a high CO2 gas generator.
The content may be increased.
【0048】該調製により熱が発生するので、この工程
にはさらに外部との熱交換を含めるのが好ましい。それ
によって温度が十分低く、典型的には40℃から80℃
の間に保たれ、反応をできるだけ短時間に終えることが
できる。熱交換器16はそのために設けられている。Since heat is generated by the preparation, it is preferable that this step further includes heat exchange with the outside. This allows the temperature to be low enough, typically 40 ° C to 80 ° C
It is kept for a short time, and the reaction can be completed in the shortest possible time. The heat exchanger 16 is provided for that purpose.
【0049】使用済み吸着剤を炭酸アンモニウム溶液に
接触させる再生段階そのものは以下の反応機序によって
行われる。 CaSO4+(NH4)2CO3 CaCO3+(NH4)2SO4The regeneration step itself, in which the used adsorbent is brought into contact with the ammonium carbonate solution, is carried out by the following reaction mechanism. CaSO4 + (NH4) 2CO3 CaCO3 + (NH4) 2SO4
【0050】使用済み吸着剤にはかなりの量、場合によ
って30%から70%台の生石灰が含まれており、純粋
な無水物でできているわけではない。これを直接反応器
17-aに装入してもよく、あるいは生石灰を消石灰に
転換するために水および/または蒸気で最初の消和を行
ってもよい。この再生段階で、媒体温度を調節するため
に外部との交換も1回あるいは数回行う。熱交換は、吸
着剤の性質(特にその硫酸化率)により、また前以て消
和を行ったかどうかによってエネルギーを供給したりあ
るいは抽出して行う。手段19によってこの熱交換を行
う。The spent adsorbent contains a significant amount, sometimes 30% to 70%, of quicklime, and is not made of pure anhydrous. It may be charged directly into reactor 17-a, or it may be first slaked with water and / or steam to convert quicklime to slaked lime. At this regeneration stage, exchange with the outside is performed once or several times to adjust the medium temperature. The heat exchange is carried out by supplying or extracting energy depending on the nature of the adsorbent (in particular, its sulfation rate) and whether or not the adsorbent has been preliminarily digested. This heat exchange is performed by means 19.
【0051】再生は、無水物をできるだけ完全に硫酸ア
ンモニウムに転換するために単一の反応器ではなく連続
して配列した反応器17-a、17-b・・・で行うのが好
ましい。The regeneration is preferably carried out in a series of reactors 17-a, 17-b ... Instead of a single reactor in order to convert the anhydride to ammonium sulfate as completely as possible.
【0052】17-a、17-b・・・の各反応器に攪拌手
段18が設けられている場合は効率よく混合することが
できる。When the stirring means 18 is provided in each of the reactors 17-a, 17-b ..., Mixing can be performed efficiently.
【0053】しかも、炭酸アンモニウム、二酸化炭素溶
液あるいは他の化合物を一連の反応器の数カ所で追加す
ることができ、反応を促進できる。In addition, ammonium carbonate, carbon dioxide solution or other compounds can be added at several points in the series of reactors to accelerate the reaction.
【0054】再生工程を終えた(ライン23を介した)
混合物はその後炭酸カルシウムと消石灰を回収するため
にフィルター22に通す。この濾過工程は例えば水を逆
流させて行い、ライン25次いでライン3bを通って発
熱器の脱硫脱窒室1-bに再注入される吸着剤の残留硫
酸アンモニウム濃度を抑制する。Finished the regeneration process (via line 23)
The mixture is then passed through a filter 22 to recover calcium carbonate and slaked lime. This filtration step is performed, for example, by backflowing water to suppress the residual ammonium sulfate concentration of the adsorbent that is re-injected into the desulfurization and denitrification chamber 1-b of the heat generator through the line 25 and then the line 3b.
【0055】再生吸着剤は、発熱器1で再使用する前に
さらに処理するのが好ましい。例えば、乾燥した形で使
用する場合は乾燥工程、懸濁液の形で使用する場合は媒
体の水分調整を行ったり該懸濁液の安定剤を添加するな
どである。The regenerated adsorbent is preferably further processed before reuse in the heating element 1. For example, when it is used in a dried form, it is a drying process, and when it is used in the form of a suspension, the water content of the medium is adjusted, and a stabilizer for the suspension is added.
【0056】図面のライン26は水の供給ラインであ
る。Line 26 in the drawing is a water supply line.
【0057】最後に、濾過工程を終えた高濃度硫酸アン
モニウム溶液はライン24を通って既知の固化手段に送
り、得た固体は単独で肥料として使用してもよく、ある
いはさらに複雑な組成の肥料の成分として用いてもよ
い。Finally, the high-concentration ammonium sulfate solution that has undergone the filtration step is sent to a known solidifying means through a line 24, and the obtained solid may be used alone as a fertilizer, or a fertilizer having a more complicated composition may be used. You may use it as an ingredient.
【0058】かかる溶液を得ることにより、本発明は非
常に経済的な利点を有する。事実、公知の機序によれ
ば、使用済みの吸着剤の再生によって、硫黄が濃縮SO
2およびH2Sの形で放出され、これらの化学物質は特定
の装置(クラウスプラントなど)に供給して硫黄を元素
に転換しなければならない。By obtaining such a solution, the present invention has very economic advantages. In fact, according to known mechanisms, the regeneration of the spent adsorbent results in sulfur enriched SO
Emitted in the form of 2 and H2S, these chemicals must be fed to specific equipment (such as the Claus plant) to convert sulfur to elements.
【0059】本発明によって最終的に得られる高濃度硫
酸アンモニウム溶液は肥料の高品質化を可能にし、それ
によって従来の硫黄チャンネルの飽和を避けることがで
きる。The highly concentrated ammonium sulphate solution finally obtained according to the invention makes it possible to improve the quality of the fertilizer and thus avoid the conventional saturation of sulfur channels.
【0060】もちろん、本発明の範囲から逸脱すること
なく、本技術分野の熟練者であれば上記プラントおよび
プロセスに種々の改良、追加を行うことができる。Of course, those skilled in the art can make various improvements and additions to the above plant and process without departing from the scope of the present invention.
【0061】ここに記載のプロセスは、本発明による再
生によって良好な脱硫効果を持つ粉状の吸着剤が得られ
るため、微小粒径の吸着剤を用いるキャリードベッド
(carried bed)発熱器に適しているが、稠密あるいは
循環流動床炉など、その場で脱硫を行う他の技術にも応
用できる。The process described here is suitable for a carried bed heater with a fine particle size adsorbent, since the regeneration according to the invention gives a powdery adsorbent with a good desulfurization effect. However, it can also be applied to other in situ desulfurization techniques such as dense or circulating fluidized bed furnaces.
【図面】 本発明によるプラントの実施例の概略図。FIG. 1 is a schematic view of an embodiment of a plant according to the present invention.
───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 C01C 1/10 A 6908−3K F23J 15/00 J ─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification code Internal reference number FI technical display location C01C 1/10 A 6908-3K F23J 15/00 J
Claims (14)
-b)を有する発熱器(1)と、燃焼フュームを除塵す
るための手段(6)と、手段(6)からの排出ガスを排
出する煙突と、使用済み吸着剤を再生する手段(17)
と、再生吸着剤を濾過する手段(22)とからなる発熱
プラントにおいて、使用する吸着剤が石灰質の物質であ
り、濾過手段(22)からでる硫黄含有物質が肥料であ
り、プラントがさらに再生のための溶液を調製する手段
(9)を含み、該手段には貯留手段(4)が供給するア
ンモニア溶液を除塵手段(6)からでるガスの一部と接
触させ、その溶液に手段(14)に貯留した二酸化炭素
を添加するようにした交換器(9)が含まれ、該手段
(9)でそのようにして調製された溶液が濃縮炭酸アン
モニウム溶液であることを特徴とする発熱プラント。1. A desulfurization / denitrification zone (1) utilizing an adsorbent.
a heat generator (1) having -b), means (6) for removing dust from combustion fumes, a chimney for discharging exhaust gas from the means (6), and means (17) for regenerating used adsorbent
And a means (22) for filtering the regenerated adsorbent, the adsorbent used is a calcareous substance, the sulfur-containing substance emitted from the filtration means (22) is a fertilizer, and the plant is further regenerated. Means (9) for preparing a solution for the purpose of contacting the ammonia solution supplied by the storage means (4) with a part of the gas emitted from the dust removing means (6), and bringing the solution into the solution (14). A heat-generating plant, characterized in that it comprises an exchanger (9) adapted to add the carbon dioxide stored therein and the solution thus prepared by said means (9) is a concentrated ammonium carbonate solution.
熱交換器(16)を含むことを特徴とする請求項1に記
載のプラント。2. Plant according to claim 1, characterized in that it further comprises a heat exchanger (16) operating in cooperation with said means (9).
/または脱窒室(1-b)、対流交換器(1-c)を含
み、該室(1-b)が再生吸着剤、非再生吸着剤および
貯留手段(4)が供給する水酸化アンモニウムを配送す
るための供給ライン(2、3-a、3-b)を含むことを
特徴とする請求項1または2に記載のプラント。3. The heat generator includes a combustion chamber (1-a), a desulfurization and / or denitrification chamber (1-b) and a convection exchanger (1-c), the chamber (1-b) being regenerated and adsorbed. 3. A supply line (2,3-a, 3-b) for delivering the agent, the non-regenerated adsorbent and the ammonium hydroxide supplied by the storage means (4). Plant.
ム溶液と塵埃分離器(6)からでる使用済み石灰質吸着
剤の一部とが供給される少なくとも1基の反応器(17
-a)を含み、該反応器には混合液を攪拌するための手
段(18)が設けられていることを特徴とする請求項1
乃至3のいずれかに記載のプラント。4. The adsorbent regeneration means is at least one reactor (17) to which the concentrated ammonium carbonate solution and a part of the spent calcareous adsorbent discharged from the dust separator (6) are supplied.
-a), wherein the reactor is provided with means (18) for stirring the mixture.
4. The plant according to any one of 3 to 3.
に熱回収手段(19)が含まれていることを特徴とする
請求項4に記載のプラント。5. Plant according to claim 4, characterized in that at least one of the reactors further comprises a heat recovery means (19).
う − 処理ずみ排出ガスの熱交換を行う − 処理ずみ排出ガスの除塵を行う − 吸着剤を回収し、その一部を脱硫/脱窒ゾーンに向
けて再循環させ、残りを再生ゾーンに供給する − 除塵したフュームを大気中に放出する − 吸着剤を再生する − 再生吸着剤を脱硫/脱窒ゾーンに再循環させる − 再生段階で出たフュームを排出する 工程からなる発熱プロセスにおいて、該プロセスが − 石灰質吸着剤を使用する − (i)再生工程の前に、水酸化アンモニウムと、一部
が発熱器(1)のフューム および/または特定の容
器からの二酸化炭素で濃縮炭酸アンモニウム溶液を
調製する − 再生工程中、少なくとも1基の反応器で該溶液と再
生しようとする石灰質吸着剤とを混合する − 該再生工程で得た混合液を濾過する − 再生済み石灰質吸着剤を脱硫/脱窒ゾーンに再循環
させる前に、該吸着剤を回収する(ライン25)一方、
硫酸アンモニウム溶液も回収する(ライン24)工程か
らなることを特徴とする発熱プロセス。6. Combustion in a heat generator-Desulfurization and denitrification of exhaust gas from combustion in the heat generator-Heat exchange of treated exhaust gas-Dust removal of treated exhaust gas- Collect the adsorbent, recirculate a part of it to the desulfurization / denitrification zone, and supply the rest to the regeneration zone.- Release dust-removed fumes into the atmosphere-Regenerate adsorbent-Regenerated adsorbent Recycle to desulfurization / denitrification zone-in an exothermic process consisting of discharging fumes from the regeneration stage, the process-using a calcareous adsorbent- (i) prior to the regeneration process ammonium hydroxide and , Part of the fumes of the heat generator (1) and / or concentrated ammonium carbonate solution with carbon dioxide from a specific container
Prepare-mix the solution with the calcareous adsorbent to be regenerated in at least one reactor during the regeneration process-filter the mixture obtained in the regeneration process-desulfurize / desulfurize the regenerated calcareous adsorbent Before recirculating to the nitrification zone, the adsorbent is recovered (line 25) while
An exothermic process comprising a step of recovering also ammonium sulfate solution (line 24).
よび/または吸着剤再生と同時に熱交換を行うことを特
徴とする請求項6に記載のプロセス。7. Process according to claim 6, characterized in that the heat exchange is carried out simultaneously with the preparation of the ammonium carbonate solution and / or the regeneration of the adsorbent.
行われることを特徴とする請求項7に記載のプロセス。8. Process according to claim 7, characterized in that the preparation is carried out at a temperature between 40 ° C. and 80 ° C.
7-b・・・)で連続して行われることを特徴とする請求項
6乃至8のいずれかに記載のプロセス。9. Reactor having several reactors (17-a, 1)
7-b ...) are carried out consecutively, the process according to any one of claims 6 to 8.
素の供給が種々の反応器においてさらに行われることを
特徴とする請求項9に記載のプロセス。10. Process according to claim 9, characterized in that the supply of calcium carbonate and / or carbon dioxide is additionally carried out in different reactors.
行われることを特徴とする請求項6乃至10のいずれか
に記載のプロセス。11. Process according to any of claims 6 to 10, characterized in that the filtering step is carried out by backflowing water.
らに追加処理することを特徴とする請求項6乃至11の
いずれかに記載のプロセス。12. The process according to any one of claims 6 to 11, wherein the regenerated adsorbent is further treated after recovery before being recycled.
請求項12に記載のプロセス。13. The process according to claim 12, wherein the additional treatment is drying.
定剤の追加供給であることを特徴とする請求項12に記
載のプロセス。14. Process according to claim 12, characterized in that the additional treatment is regulation of water content and / or additional supply of stabilizer.
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
FR93/12905 | 1993-10-26 | ||
FR9312905A FR2711549B1 (en) | 1993-10-26 | 1993-10-26 | Process and installation for generating heat with regeneration of the absorbent and obtaining a fertilizing product. |
Publications (1)
Publication Number | Publication Date |
---|---|
JPH07180828A true JPH07180828A (en) | 1995-07-18 |
Family
ID=9452329
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP6286055A Pending JPH07180828A (en) | 1993-10-26 | 1994-10-26 | Heat-generation process and plant simultaneously functioningas regeneration of adsorbent and fertilizer production |
Country Status (7)
Country | Link |
---|---|
EP (1) | EP0649674B1 (en) |
JP (1) | JPH07180828A (en) |
KR (1) | KR950010940A (en) |
CN (1) | CN1108744A (en) |
DE (1) | DE69425538T2 (en) |
FR (1) | FR2711549B1 (en) |
TW (1) | TW253932B (en) |
Families Citing this family (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
TWI510283B (en) * | 2013-08-19 | 2015-12-01 | Univ Chang Gung | Waste gas desulfurization method |
CN112495140A (en) * | 2020-10-16 | 2021-03-16 | 义乌韦陀环保科技有限公司 | VOCs exhaust-gas treatment system |
Family Cites Families (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
FR2156953A5 (en) * | 1971-10-11 | 1973-06-01 | Inst Francais Du Petrole | |
GB2068919A (en) * | 1980-02-12 | 1981-08-19 | Conoco Inc | Method for regenerating calcium sulfoxy compounds produced in the combustion of carbonaceous fuels in fluidized beds |
DE3217394A1 (en) * | 1982-05-08 | 1983-11-10 | Saarbergwerke AG, 6600 Saarbrücken | Process for treating calcium sulphate from flue gas desulphurisation units |
US4956161A (en) * | 1989-01-13 | 1990-09-11 | Exxon Research And Engineering Company | Process for removing SO from a gaseous mixture (OP-3409) |
-
1993
- 1993-10-26 FR FR9312905A patent/FR2711549B1/en not_active Expired - Fee Related
-
1994
- 1994-10-20 TW TW083109705A patent/TW253932B/zh active
- 1994-10-24 EP EP94402389A patent/EP0649674B1/en not_active Expired - Lifetime
- 1994-10-24 DE DE69425538T patent/DE69425538T2/en not_active Expired - Fee Related
- 1994-10-25 KR KR1019940027252A patent/KR950010940A/en active IP Right Grant
- 1994-10-26 CN CN94116035A patent/CN1108744A/en active Pending
- 1994-10-26 JP JP6286055A patent/JPH07180828A/en active Pending
Also Published As
Publication number | Publication date |
---|---|
TW253932B (en) | 1995-08-11 |
DE69425538T2 (en) | 2001-01-04 |
EP0649674A1 (en) | 1995-04-26 |
KR950010940A (en) | 1995-05-15 |
DE69425538D1 (en) | 2000-09-21 |
FR2711549A1 (en) | 1995-05-05 |
CN1108744A (en) | 1995-09-20 |
FR2711549B1 (en) | 1996-01-26 |
EP0649674B1 (en) | 2000-08-16 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN104001403B (en) | The technique of a kind of activated coke/charcoal flue gas desulfurization and denitrification and recovery elemental sulfur and device | |
RU2040960C1 (en) | Method and apparatus to remove sulfur oxides from furnace gasses | |
WO2008052465A1 (en) | A sintered flue gas wet desulfurizing and dedusting process | |
CN103721557A (en) | Desulfurization in a regenerative calcium cycle system | |
JPH0421524B2 (en) | ||
WO2017019283A1 (en) | Sulfur enhanced nitrogen production from emission scrubbing | |
CN106621808A (en) | Wet type integrated purification system and method for recovery of residual heat in flue gas | |
EP0097240B1 (en) | Process for removal of sulfur oxides from hot gases | |
US6079212A (en) | Gasification power generation process and gasification power generation equipment | |
KR100240327B1 (en) | Heat generating installation having desulfurization means using regeneratable absorbents | |
JP2977759B2 (en) | Exhaust gas dry treatment method and apparatus | |
JPS6372322A (en) | Method of removing sulfur dioxide from flue gas | |
JP2013202434A (en) | Method for disposing of fluidized bed-system boiler ash and disposer | |
JPH07180828A (en) | Heat-generation process and plant simultaneously functioningas regeneration of adsorbent and fertilizer production | |
US4686090A (en) | Desulfurizing of reducing gas stream using a recycle calcium oxide system | |
DE102007005578A1 (en) | Exhaust gas desulfurization method, involves concentrating part of working solution in heated desorber before it is again supplied to solution, condensing produced desorber vapor, and delivering vapor as distillate | |
WO1994021965A1 (en) | Recycling processes using fly ash | |
KR100303388B1 (en) | Aaaaa | |
KR820001196B1 (en) | Process for production of h s from so obtained from flue gas | |
JPS62277127A (en) | Removal of sulfur oxide from gaseous and/or liquid waste | |
JP2811005B2 (en) | Method and apparatus for incineration and desulfurization in a circulating bed of a gaseous effluent containing incompletely combusted gas and SO2, SO3 and / or H2S | |
JPH08131777A (en) | Exhaust gas treatment method | |
EP0643987A2 (en) | Bioregenerative flue gas desulphurization | |
JPH07106293B2 (en) | Refining method for high temperature reducing gas | |
JPH0788332A (en) | Treatment of waste gas |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
A131 | Notification of reasons for refusal |
Free format text: JAPANESE INTERMEDIATE CODE: A131 Effective date: 20040303 |
|
A02 | Decision of refusal |
Free format text: JAPANESE INTERMEDIATE CODE: A02 Effective date: 20040728 |